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Frontiers of Earth Science

ISSN 2095-0195

ISSN 2095-0209(Online)

CN 11-5982/P

Postal Subscription Code 80-963

2018 Impact Factor: 1.205

Front. Earth Sci.    2019, Vol. 13 Issue (1) : 92-110    https://doi.org/10.1007/s11707-018-0713-0
RESEARCH ARTICLE
Spatio-temporal analysis of phenology in Yangtze River Delta based on MODIS NDVI time series from 2001 to 2015
Yongfeng WANG1, Zhaohui XUE2(), Jun CHEN1, Guangzhou CHEN1
1. School of Environment and Engineering, Anhui Jianzhu University, Hefei 230022, China
2. School of Earth Sciences and Engineering, Hohai University, Nanjing 211100, China
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Abstract

Phenology has become a good indicator for illustrating the long-term changes in the natural resources of the Yangtze River Delta. However, two issues can be observed from previous studies. On the one hand, existing time-series classification methods mainly using a single classifier, the discrimination power, can become deteriorated due to fluctuations characterizing the time series. On the other hand, previous work on the Yangtze River Delta was limited in the spatial domain (usually to 16 cities) and in the temporal domain (usually 2000–2010). To address these issues, this study attempts to analyze the spatio-temporal variation in phenology in the Yangtze River Delta (with 26 cities, enlarged by the state council in June 2016), facilitated by classifying the land cover types and extracting the phenological metrics based on Moderate Resolution Imaging Spectrometer (MODIS) Normalized Difference Vegetation Index (NDVI) time series collected from 2001 to 2015. First, ensemble learning (EL)-based classifiers are used for land cover classification, where the training samples (a total of 201,597) derived from visual interpretation based on GlobelLand30 are further screened using vertex component analysis (VCA), resulting in 600 samples for training and the remainder for validating. Then, eleven phenological metrics are extracted by TIMESAT (a package name) based on the time series, where a seasonal-trend decomposition procedure based on loess (STL-decomposition) is used to remove spikes and a Savitzky-Golay filter is used for filtering. Finally, the spatio-temporal phenology variation is analyzed by considering the classification maps and the phenological metrics. The experimental results indicate that: 1) random forest (RF) obtains the most accurate classification map (with an overall accuracy higher than 96%); 2) different land cover types illustrate the various seasonalities; 3) the Yangtze River Delta has two obvious regions, i.e., the north and the south parts, resulting from different rainfall, temperature, and ecosystem conditions; 4) the phenology variation over time is not significant in the study area; 5) the correlation between gross spring greenness (GSG) and gross primary productivity (GPP) is very high, indicating the potential use of GSG for assessing the carbon flux.

Keywords Yangtze River Delta      MODIS NDVI      ensemble learning      land cover classification      spatio-temporal      phenology     
Corresponding Author(s): Zhaohui XUE   
Just Accepted Date: 25 July 2018   Online First Date: 06 September 2018    Issue Date: 25 January 2019
 Cite this article:   
Yongfeng WANG,Zhaohui XUE,Jun CHEN, et al. Spatio-temporal analysis of phenology in Yangtze River Delta based on MODIS NDVI time series from 2001 to 2015[J]. Front. Earth Sci., 2019, 13(1): 92-110.
 URL:  
https://academic.hep.com.cn/fesci/EN/10.1007/s11707-018-0713-0
https://academic.hep.com.cn/fesci/EN/Y2019/V13/I1/92
Fig.1  Yangtze River Delta covering 26 cities from Jiangsu, Zhejiang, and Anhui provinces, including Shanghai City.
Fig.2  Land cover reference maps for Yangtze River Delta. (a) GlobeLand30, (b) Regions of interest chosen from GlobeLand30.
Fig.3  Flowchart of the methodology used in this study.
Fig.4  A toy example of VCA for pure sample selection. The points with different colors represent specific land cover types, and the points in the circle are likely to be the endmembers.
Fig.5  Graphical illustration of an ensemble learning-based classification scheme. The notation is as follows: Bagging- ensemble learning based on bootstrap; RoF- Rotation Forest; RS- Random Subspace; and RF- Random Forest.
Fig.6  Graphical illustration of the phenological metrics (Xue et al., 2014a).
Name Deftnition Abbreviation Description in Fig. 6
Start of season Timing determined by seasonal level 50% before mid-season SOS a
End of season Timing determined by seasonal level 50% after mid-season EOS b
Length of season Time from SOS to EOS LOS g
Base level of season Average value of the base line under time series BOS h
Timing of mid-season The mean timing between c and d TOMS i
Peak value of season The maximum value of time series POS e
Amplitude of season The difference between POS and BOS AOS f
Rate of grow-up The average slope between a and c ROG
Rate of senescence The average slope between b and d ROS
Gross spring greenness The area covered by the fttted curve and the base level h between SOS and EOS GSG S2
Net spring greenness The area covered by the Fitted curve and the senescence level j between SOS and EOS NSG S1
Tab.1  Definitions, abbreviations, and properties of different phenological metrics
Fig.7  Overall accuracy (OA) as a function of number of labeled samples per class. The notation is as follows: kNN- k nearest neighbor; LORSAL- multinomial logistic regression via variable splitting and augmented Lagrangian; SRC- sparse representation-based classification method; Bagging- ensemble learning based on bootstrap; RoF- Rotation Forest; RS- Random Subspace; and RF- Random Forest.
Class Train Test Classification methods
kNN SVM LORSAL SRC Bagging RoF RS RF
Cultivated land 100 73702 92.00 96.26 92.81 88.50 94.76 92.42 88.66 96.61
Forest 100 51984 99.53 99.73 99.35 99.98 97.64 98.45 98.45 98.40
Grassland 100 1109 85.11 89.91 96.69 98.76 89.50 90.07 88.92 91.15
Wetland 100 1638 50.35 94.02 78.71 98.62 93.90 73.71 92.81 98.73
Water bodies 100 47042 93.89 89.02 85.96 82.10 98.04 96.41 93.89 93.48
Artiftcial surfaces 100 25522 99.50 92.30 94.98 42.59 97.97 99.02 99.68 99.12
Average accuracy - - 86.73 93.54 91.42 85.09 95.30 91.68 93.73 96.25
Overall accuracy - - 94.94 94.90 93.08 84.28 96.64 95.57 93.85 96.64
k statistic - - 0.931 0.931 0.906 0.786 0.954 0.940 0.917 0.954
Tab.2  A comparison of different classifiers in terms of class-specific accuracy, OA, AA, k (100 labeled samples per class)
Classifier Statistical test between-classifier
k (z-score) McNemar (z-score)
kNN/RF 26.95 1.83E+3
SVM/RF 27.67 1.25E+3
LORSAL/RF 51.74 2.92E+3
SRC/RF 141.37 2.00E+3
Bagging/RF 0.17* 0.02*
RoF/RF 17.56 0.43E+3
RS/RF 41.53 4.19E+3
Tab.3  Statistical test between-classifter in terms of Kappa z-score and McNemar z-score (100 labeled samples per class)
Fig.8  Classification maps obtained by (a) kNN, (b) SVM, (c) LORSAL, (d) SRC, (e) Bagging, (f) RoF, (g) RS, and (h) RF. The following notation is used: kNN- k nearest neighbor; SVM- support vector machine; LORSAL- multinomial logistic regression via variable splitting and augmented Lagrangian; SRC- sparse representation-based classification method; Bagging- ensemble learning based on bootstrap; RoF- Rotation Forest; RS- Random Subspace; and RF- Random Forest.
Class Phenological metrics
SOS EOS LOS BOS TOMS POS AOS ROG ROS GSG NSG
Cultivated land 180.1 294.3 114.3 3476.3 244.5 7686.8 4210.6 447.6 946.3 57894.3 26720.7
Forest 118.6 322.5 204.1 5661.1 214.8 8445.8 2784.7 608.1 368.7 115426.4 32567.9
Grassland 79.1 174.0 94.7 2359.1 124.1 6683.2 4324.2 949.8 787.3 42095.0 23691.4
Wetland 134.3 308.2 173.9 718.7 230.5 4066.3 3347.6 379.0 505.1 41337.9 32071.4
Water bodies 130.2 318.3 188.1 ?935.7 235.4 299.4 1235.0 95.2 194.9 ?454.2 12342.9
Artiftcial surfaces 111.8 310.7 198.8 2017.7 215.8 3990.7 1973.0 252.6 263.6 50868.6 21800.7
Tab.4  Typical land cover phenological metrics after averaging the results obtained from 2001 to 2015
Fig.9  Typical land cover seasonal analysis with Raw and Fitted series marked as SOS (start of season) and EOS (end of season). (a) Cultivated land, (b) Forest, (c) Grassland, (d) Wetland, (e) Water bodies, and (f) Artificial surfaces.
Fig.10  Spatial visualization of averaged phenological metrics obtained from 2001 to 2015. (a) SOS, (b) EOS, (c) LOS, (d) BOS, (e) TOMS, (f) POS, (g) AOS, (h) ROG, (i) ROS, (j) GSG, and (k) NSG. The following notation is used: SOS- start of season; EOS- end of season; LOS- length of season; BOS- base level of season; TOMS- timing of mid-season; POS- peak value of season; AOS- amplitude of season; ROG- rate of grow-up; ROS- rate of senescence; GSG- gross spring greenness; and NSG- net spring greenness.
Fig.11  The values of different phenological metrics (as a function of year) obtained for different land covers. (a) SOS, (b) EOS, (c) LOS, (d) BOS, (e) TOMS, (f) POS, (g) AOS, (h) ROG, (i) ROS, (j) GSG, and (k) NSG. The following notation is used: SOS- start of season; EOS- end of season; LOS- length of season; BOS- base level of season; TOMS- timing of mid-season; POS- peak value of season; AOS- amplitude of season; ROG- rate of grow-up; ROS- rate of senescence; GSG- gross spring greenness; and NSG- net spring greenness.
Fig.12  Correlation analysis of SOS and EOS with the yearly accumulated rainfall and the average temperature. (a) SOS vs. rainfall; (b) EOS vs. rainfall; (c) SOS vs. temperature; (d) EOS vs. temperature.
Fig.13  Correlation analysis of GPP versus GSG.
1 S PAbercrombie, M AFriedl (2016). Improving the consistency of multitemporal land cover maps using a hidden Markov model. IEEE Trans Geosci Remote Sens, 54(2): 703–713
https://doi.org/10.1109/TGRS.2015.2463689
2 M CAnderson, C A Zolin, P C Sentelhas, C R Hain, K Semmens, MTugrul Yilmaz, FGao, J AOtkin, RTetrault (2016). The evaporative stress index as an indicator of agricultural drought in Brazil: an assessment based on crop yield impacts. Remote Sens Environ, 174: 82–99
https://doi.org/10.1016/j.rse.2015.11.034
3 LBreiman (1996). Bagging predictors. Mach Learn, 24(2):123–140
4 LBreiman (2001) Random forests. Mach Learn, 45(1): 5–32
https://doi.org/10.1023/A:1010933404324
5 JChen, J Chen, A PLiao, XCao, L J Chen, X H Chen, S Peng, GHan, H WZhang, C YHe, HWu, M Lu (2014). Concepts and key techniques for 30 m global land cover mapping. Acta Geodaetica et Cartographica Sinica, 43(6): 551–557
6 JChen, P Jonsson, MTamura, Z HGu, BMatsushita, LEklundh (2004). A simple method for reconstructing a high-quality NDVI time-series data set based on the Savitzky-Golay filter. Remote Sens Environ, 91(3‒4): 332–344
https://doi.org/10.1016/j.rse.2004.03.014
7 JChen, Y H Rao, M G Shen, C Wang, YZhou, LMa, Y H Tang, X Yang (2016). A simple method for detecting phenological change from time series of vegetation index. IEEE Trans Geosci Remote Sens, 54(6): 3436–3449
https://doi.org/10.1109/TGRS.2016.2518167
8 KClauss, H M Yan, C Kuenzer (2016). Mapping paddy rice in China in 2002, 2005, 2010 and 2014 with MODIS time series. Remote Sens, 8(5): 434
https://doi.org/10.3390/rs8050434
9 CCortes, V Vapnik (1995). Support-vector networks. Mach Learn, 20(3): 273–297
https://doi.org/10.1007/BF00994018
10 T MCover, P E Hart (1967). Nearest neighbor pattern classification. IEEE Trans Inf Theory, 13(1): 21–27
https://doi.org/10.1109/TIT.1967.1053964
11 BDemir, F Bovolo, LBruzzone (2013). Updating land-cover maps by classification of image time series: a novel change-detection-driven transfer learning approach. IEEE Trans Geosci Remote Sens, 51(1): 300–312
https://doi.org/10.1109/TGRS.2012.2195727
12 P JDu, J S Xia, W Zhang, KTan, YLiu, S C Liu (2012). Multiple classifier system for remote sensing image classification: a review. Sensors (Basel), 12(4): 4764–4792
https://doi.org/10.3390/s120404764
13 LEklundh, P Jönsson (2015). Timesat 3.2 software mannual. Lund and Malmö University, Sweden
14 RFensholt, SR Proud (2012). Evaluation of earth observation based global long term vegetation trends- Comparing GIMMS and MODIS global NDVI time series. Remote Sens Environ, 119: 131–147
https://doi.org/10.1016/j.rse.2011.12.015
15 MFernandez-Delgado, ECernadas, SBarro, DAmorim (2014). Do we need hundreds of classifiers to solve real world classification problems? J Mach Learn Res, 15: 3133–3181
16 G MFoody (2004). Thematic map comparison: evaluating the statistical significance of differences in classification accuracy. Photogramm Eng Remote Sensing, 70(5): 627–633
https://doi.org/10.14358/PERS.70.5.627
17 SGhosh, D R Mishra, A A Gitelson (2016). Long-term monitoring of biophysical characteristics of tidal wetlands in the northern Gulf of Mexico−A methodological approach using MODIS. Remote Sens Environ, 173: 39–58 doi:10.1016/j.rse.2015.11.015
18 CGómez, J C White, M A Wulder (2016). Optical remotely sensed time series data for land cover classification: a review. ISPRS J Photogramm Remote Sens, 116: 55–72
https://doi.org/10.1016/j.isprsjprs.2016.03.008
19 X DGuan, C Huang, G HLiu, X LMeng, Q SLiu (2016). Mapping rice cropping systems in Vietnam using an NDVI-based time-series similarity measurement based on DTW distance. Remote Sens, 8(1): 19
https://doi.org/10.3390/rs8010019
20 G FHan, J H Xu (2013). Land surface phenology and land surface temperature changes along an urban-rural gradient in Yangtze River Delta, China. Environ Manage, 52(1): 234–249
https://doi.org/10.1007/s00267-013-0097-6
21 SHeremans, J A K Suykens, J Van Orshoven (2016). The effect of imposing ‘fractional abundance constraints’ onto the multilayer perceptron for sub-pixel land cover classification. Int J Appl Earth Obs Geoinf, 44: 226–238
https://doi.org/10.1016/j.jag.2015.09.007
22 GHmimina, E Dufrêne, J YPontailler, NDelpierre, MAubinet, BCaquet, Ade Grandcourt, BBurban, CFlechard, AGranier, PGross, BHeinesch, BLongdoz, CMoureaux, J MOurcival, SRambal, LSaint André, KSoudani (2013). Evaluation of the potential of MODIS satellite data to predict vegetation phenology in different biomes: an investigation using ground-based NDVI measurements. Remote Sens Environ, 132: 145–158
https://doi.org/10.1016/j.rse.2013.01.010
23 T KHo (1998). The random subspace method for constructing decision forests. IEEE Trans Pattern Anal Mach Intell, 20(8): 832–844
https://doi.org/10.1109/34.709601
24 AHuete, K Didan, TMiura, E PRodriguez, XGao, L G Ferreira (2002). Overview of the radiometric and biophysical performance of the MODIS vegetation indices. Remote Sens Environ, 83(1‒2): 195–213
https://doi.org/10.1016/S0034-4257(02)00096-2
25 PJönsson, L Eklundh (2002). Seasonality extraction by function fitting to time-series of satellite sensor data. IEEE Trans Geosci Remote Sens, 40(8): 1824–1832
https://doi.org/10.1109/TGRS.2002.802519
26 KKaralas, G Tsagkatakis, MZervakis, PTsakalides (2016). Land classification using remotely sensed data: going multilabel. IEEE Trans Geosci Remote Sens, 54(6): 3548–3563
https://doi.org/10.1109/TGRS.2016.2520203
27 JLi, J M Bioucas-Dias, A Plaza (2011). Hyperspectral image segmentation using a new Bayesian approach with active learning. IEEE Trans Geosci Remote Sens, 49(10): 3947–3960
https://doi.org/10.1109/TGRS.2011.2128330
28 M MLi, Z C Mao, Y Song, M XLiu, XHuang (2015). Impacts of the decadal urbanization on thermally induced circulations in eastern China. J Appl Meteorol Climatol, 54(2): 259–282
https://doi.org/10.1175/JAMC-D-14-0176.1
29 C GMarston, P Giraudoux, R PArmitage, F MDanson, S CReynolds, QWang, J M Qiu, P S Craig (2016). Vegetation phenology and habitat discrimination: impacts for E. multilocularis transmission host modelling. Remote Sens Environ, 176: 320–327
https://doi.org/10.1016/j.rse.2016.02.015
30 J M PNascimento, J M BDias (2005). Vertex component analysis: a fast algorithm to unmix hyperspectral data. IEEE Trans Geosci Remote Sens, 43(4): 898–910
https://doi.org/10.1109/TGRS.2005.844293
31 S HQader, J Dash, P MAtkinson, VRodriguez-Galiano (2016). Classification of vegetation type in Iraq using satellite-based phenological parameters. IEEE J Sel Top Appl Earth Obs Remote Sens, 9(1): 414–424
https://doi.org/10.1109/JSTARS.2015.2508639
32 B WQiu, M Feng, Z HTang (2016). A simple smoother based on continuous wavelet transform: comparative evaluation based on the fidelity, smoothness and efficiency in phenological estimation. Int J Appl Earth Obs Geoinf, 47: 91–101
https://doi.org/10.1016/j.jag.2015.11.009
33 J JRodriguez, L IKuncheva, C JAlonso (2006). Rotation forest: a new classifier ensemble method. IEEE Trans Pattern Anal Mach Intell, 28(10): 1619–1630
https://doi.org/10.1109/TPAMI.2006.211
34 YShao, R S Lunetta, B Wheeler, J SIiames, J BCampbell (2016). An evaluation of time-series smoothing algorithms for land-cover classifications using MODIS-NDVI multi-temporal data. Remote Sens Environ, 174: 258–265
https://doi.org/10.1016/j.rse.2015.12.023
35 J JShi, J F Huang (2015). Monitoring spatio-temporal distribution of rice planting area in the Yangtze River Delta region using MODIS images. Remote Sens, 7(7): 8883–8905
https://doi.org/10.3390/rs70708883
36 JVerbesselt, R Hyndman, GNewnham, DCulvenor (2010). Detecting trend and seasonal changes in satellite image time series. Remote Sens Environ, 114(1): 106–115
https://doi.org/10.1016/j.rse.2009.08.014
37 AVerger, I Filella, FBaret, JPenuelas (2016). Vegetation baseline phenology from kilometric global LAI satellite products. Remote Sens Environ, 178: 1–14
https://doi.org/10.1016/j.rse.2016.02.057
38 B DWardlow, S L Egbert, J H Kastens (2007). Analysis of time-series MODIS 250 m vegetation index data for crop classification in the US Central Great Plains. Remote Sens Environ, 108(3): 290–310
https://doi.org/10.1016/j.rse.2006.11.021
39 H YWei, P Heilman, J GQi, M ANearing, Z HGu, Y GZhang (2012). Assessing phenological change in China from 1982 to 2006 using AVHRR imagery. Front Earth Sci, 6(3): 227–236
https://doi.org/10.1007/s11707-012-0321-3
40 CWohlfart, G H Liu, C Huang, CKuenzer (2016). A river basin over the course of time: multi-temporal analyses of land surface dynamics in the Yellow River Basin (China) based on medium resolution remote sensing data. Remote Sens, 8(3): 186
https://doi.org/10.3390/rs8030186
41 JWright, A Y Yang, A Ganesh, S SSastry, YMa (2009). Robust face recognition via sparse representation. IEEE Trans Pattern Anal Mach Intell, 31(2): 210–227
https://doi.org/10.1109/TPAMI.2008.79
42 J SXia, M Dalla Mura, JChanussot, P JDu, X YHe (2015). Random subspace ensembles for hyperspectral image classification with extended morphological attribute profiles. IEEE Trans Geosci Remote Sens, 53(9): 4768–4786
https://doi.org/10.1109/TGRS.2015.2409195
43 J SXia, P J Du, X Y He, J Chanussot (2014). Hyperspectral remote sensing image classification based on rotation forest. IEEE Geosci Remote Sens Lett, 11(1): 239–243
https://doi.org/10.1109/LGRS.2013.2254108
44 Z HXue, P J Du, L Feng (2014a). Phenology-driven land cover classification and trend analysis based on long-term remote sensing image series. IEEE J Sel Top Appl Earth Obs Remote Sens, 7(4): 1142–1156
https://doi.org/10.1109/JSTARS.2013.2294956
45 Z HXue, P J Du, H J Su (2014b). Harmonic analysis for hyperspectral image classification integrated with PSO optimized SVM. IEEE J Sel Top Appl Earth Obs Remote Sens, 7(6): 2131–2146
https://doi.org/10.1109/JSTARS.2014.2307091
46 Z HXue, J Li, LCheng, P JDu (2015). Spectral-spatial classification of hyperspectral data via morphological component analysis-based image separation. IEEE Trans Geosci Remote Sens, 53(1): 70–84
https://doi.org/10.1109/TGRS.2014.2318332
47 L LZeng, B D Wardlow, R Wang, JShan, TTadesse, M JHayes, D RLi (2016). A hybrid approach for detecting corn and soybean phenology with time-series MODIS data. Remote Sens Environ, 181: 237–250
https://doi.org/10.1016/j.rse.2016.03.039
48 B HZhang, L Zhang, DXie, X LYin, C JLiu, GLiu (2016). Application of synthetic NDVI time series blended from Landsat and MODIS data for grassland biomass estimation. Remote Sensing, 8: 10
49 CZhang, Y Ma (2012). Ensemble Machine Learning. Springer Verlag New York
50 X YZhang, Q Y Zhang (2016). Monitoring interannual variation in global crop yield using long-term AVHRR and MODIS observations. ISPRS J Photogramm Remote Sens, 114: 191–205
https://doi.org/10.1016/j.isprsjprs.2016.02.010
51 BZhao, Y Yan, H QGuo, M MHe, Y JGu, BLi (2009). Monitoring rapid vegetation succession in estuarine wetland using time series MODIS-based indicators: an application in the Yangtze River Delta area. Ecol Indic, 9(2): 346–356
https://doi.org/10.1016/j.ecolind.2008.05.009
52 J JZhao, Y Y Wang, Z X Zhang, H Y Zhang, X Y Guo, S Yu, W LDu, FHuang (2016). The variations of land surface phenology in northeast China and its responses to climate change from 1982 to 2013. Remote Sens, 8(5): 400
https://doi.org/10.3390/rs8050400
53 D CZhou, S Q Zhao, L X Zhang, S G Liu (2016). Remotely sensed assessment of urbanization effects on vegetation phenology in China’s 32 major cities. Remote Sens Environ, 176: 272–281
https://doi.org/10.1016/j.rse.2016.02.010
54 C MZhu, D S Lu, D Victoria, L VDutra (2016). Mapping fractional cropland distribution in Mato Grosso, Brazil using time series MODIS enhanced vegetation index and Landsat thematic mapper data. Remote Sens, 8: 22
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